US4454102A - Method of purifying flue gases from sulphur dioxide - Google Patents

Method of purifying flue gases from sulphur dioxide Download PDF

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Publication number
US4454102A
US4454102A US06/303,462 US30346281A US4454102A US 4454102 A US4454102 A US 4454102A US 30346281 A US30346281 A US 30346281A US 4454102 A US4454102 A US 4454102A
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gas
solid absorbent
solid
phase
absorption
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US06/303,462
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Leif V. Lindau
Stefan O. H. Ahman
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ABB Technology FLB AB
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Flaekt AB
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur oxides
    • B01D53/501Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound

Definitions

  • Gases can be purified from sulfur dioxide components present therein by contacting the gas to be treated with an absorbent in a liquid phase (wet method) or in a solid phase (dry method).
  • the present invention relates to a substantially dry method.
  • the dry method includes reaction steps implying diffusion of sulfur dioxide components into a solid phase, one of its disadvantages is a relatively low reaction rate.
  • the object of the present invention is to reduce the impact of the said disadvantage. This object is achieved according to the invention characterized by the attached claim 1.
  • the absorbent may be an oxide, a carbonate or a hydroxide of an alkali metal.
  • Illustrative absorbents are calcium carbonate, magnesium calcium carbonate, sodium carbonate, calcium hydroxide, sodium hydroxide or mixtures thereof. Calcium hydroxide, sodium hydroxide or mixtures thereof are the preferred absorbents.
  • the liquid phase may be derived from a hygroscopic salt, which at the prevailing gas temperature and gas water content (water partial pressure) is a thermodynamically stable molten hydrate.
  • drying scrubbing substantially comprises a drying step and a filtering step, and it operates as follows:
  • the hot gas is contacted in a drying apparatus with an absorption liquid in the form of an atomized aqueous suspension or an aqueous solution capable of reacting with sulphur dioxide.
  • a drying apparatus evaporation of the supplied water (the water component of the atomized aqueous suspension or solution) takes place and simultaneously a reaction between sulphur dioxide and the absorbent occurs to form a solid reaction product.
  • the gas leaves the drying apparatus, the major part of the supplied water has evaporated, the gas temperature has decreased, the water vapour content of the gas has increased, and part of the sulphur dioxide has been absorbed to form the solid reaction product.
  • the gas thereafter passes a dust separator where the solid reaction product remaining and any other solid material is separated from the gas. Part of the separated dust may be further recycled into the absorption liquid in order to increase the utilization of the absorbent.
  • the present invention has also the object of bringing about a higher reaction rate during said latter process step. This is achieved by the method defined in the attached subclaims.
  • This higher reaction rate is obtained by adding to the gas a limited amount of hygroscopic substances, such as hygroscopic salts which under the conditions prevailing in the dust separator form on the surface of the solid particles a liquid aqueous phase with sufficient solubility for the reactants.
  • the hygroscopic substance may be added separately to the flue gas or may be mixed with the absorption liquid prior to its atomization.
  • the volume of the liquid phase In order to prevent the operation of the dust separator from being jeopardized, the volume of the liquid phase must be small in relation to the volume of the solid phases, and in order to achieve a good effect, the liquid phase must be well distributed over the surface of the solid phases.
  • the added hygroscopic substance may constitute a maximum of about 20 percent, and preferably is no greater than about 5 percent by volume of said solid phase present at said dust separator.
  • Examples of hygroscopic substances the hydrate of which has the property of being in the liquid phase under the conditions prevailing at the absorption of sulphur dioxide from flue gases of fossil-fired boilers, FeCl 3 , Fe(NO 3 ) 3 , Fe(NO 3 ) 2 , Al(NO 3 ) 3 , Ca(NO) 3 ) 2 , Mg(ClO 3 ) 2 , MnCl 2 , K 2 SO 4 MgSO 4 , NaAl(SO 4 ) 2 , NaClO, Na 3 PO 4 , Na 2 SiO 3 , Na 2 SO 4 or Zn(NO 3 ) 2 .
  • the absorbent added to the drying apparatus may be at least partially extracted from fly ash or gaseous substances present in or separated from the flue gas.
  • the filtering velocity of the fabric filter was 92 m/h.
  • the gas temperature after passing through the fabric filter was 70° C.
  • the following SO 2 absorption efficiencies were measured.

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  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Environmental & Geological Engineering (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Treating Waste Gases (AREA)

Abstract

Purification of gases from acid gas components according to the dry method means that the gas is contacted with an absorbent in a solid phase, which yields a relatively low reaction rate. In order to increase the reaction rate according to the invention, the gas is contacted with a mixture consisting partially of a solid absorbent phase and partially a liquid phase on the surface of the solid phase. At the purification of flue gases from sulphur dioxide hot gas is contacted with an absorption liquid in a drying apparatus, where evaporation of the water supplied and a reaction between sulphur dioxide and the absorption substance take place simultaneously, whereafter the solid product phase is separated from the gas in a dust separator and a slower, secondary absorption reaction is operative. In order to achieve a higher reaction rate in the dust separator, a substance is added to the flue gas which, together with other chemical species derived from the gas or the solid absorbent forms a liquid phase distributed over the surface of the solid phases. The liquid phase usually contains water and has a good solubility for reactants and reaction products.

Description

Gases can be purified from sulfur dioxide components present therein by contacting the gas to be treated with an absorbent in a liquid phase (wet method) or in a solid phase (dry method). The present invention relates to a substantially dry method. As the dry method includes reaction steps implying diffusion of sulfur dioxide components into a solid phase, one of its disadvantages is a relatively low reaction rate.
The object of the present invention is to reduce the impact of the said disadvantage. This object is achieved according to the invention characterized by the attached claim 1.
By effecting a liquid aqueous phase with a high solubility for the participating reactants (sulfur dioxide components) on the surface of the solid absorbent particles, the reaction steps, viz dissolving of the sulfur dioxide component, diffusion, separation of absorbent and precipitation of reaction product, proceed substantially more rapid than the corresponding reaction steps when only gaseous and solid reactants are present. The absorbent may be an oxide, a carbonate or a hydroxide of an alkali metal. Illustrative absorbents are calcium carbonate, magnesium calcium carbonate, sodium carbonate, calcium hydroxide, sodium hydroxide or mixtures thereof. Calcium hydroxide, sodium hydroxide or mixtures thereof are the preferred absorbents. The liquid phase, may be derived from a hygroscopic salt, which at the prevailing gas temperature and gas water content (water partial pressure) is a thermodynamically stable molten hydrate.
In recent years a process for absorbtion of sulphur dioxide from a hot flue gas has come into use which in the literature is referred as "dry scrubbing". The process substantially comprises a drying step and a filtering step, and it operates as follows: The hot gas is contacted in a drying apparatus with an absorption liquid in the form of an atomized aqueous suspension or an aqueous solution capable of reacting with sulphur dioxide. In the drying apparatus evaporation of the supplied water (the water component of the atomized aqueous suspension or solution) takes place and simultaneously a reaction between sulphur dioxide and the absorbent occurs to form a solid reaction product. As the gas leaves the drying apparatus, the major part of the supplied water has evaporated, the gas temperature has decreased, the water vapour content of the gas has increased, and part of the sulphur dioxide has been absorbed to form the solid reaction product. The gas thereafter passes a dust separator where the solid reaction product remaining and any other solid material is separated from the gas. Part of the separated dust may be further recycled into the absorption liquid in order to increase the utilization of the absorbent.
This process often results in incomplete utilization of the absorbent during the drying period. After said period the reaction between the sulphur dioxide and the absorbent proceeds in the dust separator. This reaction, however, proceeds relatively slowly, since the reaction steps occur in solid phases.
The present invention has also the object of bringing about a higher reaction rate during said latter process step. This is achieved by the method defined in the attached subclaims.
This higher reaction rate is obtained by adding to the gas a limited amount of hygroscopic substances, such as hygroscopic salts which under the conditions prevailing in the dust separator form on the surface of the solid particles a liquid aqueous phase with sufficient solubility for the reactants. The hygroscopic substance may be added separately to the flue gas or may be mixed with the absorption liquid prior to its atomization. As the reaction steps, viz. solution of sulphur dioxide, diffusion of reactants and precipitation of product, proceed substantially more rapid than the corresponding steps in a solid phase, the net effect thereof is an increase in the total reaction rate. In order to prevent the operation of the dust separator from being jeopardized, the volume of the liquid phase must be small in relation to the volume of the solid phases, and in order to achieve a good effect, the liquid phase must be well distributed over the surface of the solid phases. For example, the added hygroscopic substance may constitute a maximum of about 20 percent, and preferably is no greater than about 5 percent by volume of said solid phase present at said dust separator. Examples of hygroscopic substances, the hydrate of which has the property of being in the liquid phase under the conditions prevailing at the absorption of sulphur dioxide from flue gases of fossil-fired boilers, FeCl3, Fe(NO3)3, Fe(NO3)2, Al(NO3)3, Ca(NO)3)2, Mg(ClO3)2, MnCl2, K2 SO4 MgSO4, NaAl(SO4)2, NaClO, Na3 PO4, Na2 SiO3, Na2 SO4 or Zn(NO3)2.
The absorbent added to the drying apparatus may be at least partially extracted from fly ash or gaseous substances present in or separated from the flue gas.
EXAMPLE
In a pilot plant with a capacity of 10 000 Nm3 /h comprising a drying apparatus, into which atomized absorption liquid is injected, and a fabric filter as the dust separator, tests were carried out for determining the capacity with and without the addition of some of the aforesaid substances. Calcium hydroxide was used as absorbent which was added in an amount corresponding to a mole ratio Ca/SO2 =1,1 (calculated on ingoing gas). The ingoing gas had a temperature of 140° C. and an SO2 -content of 850 ppm.
The filtering velocity of the fabric filter was 92 m/h. The gas temperature after passing through the fabric filter was 70° C. The following SO2 absorption efficiencies were measured.
______________________________________                                    
Test No.     Addition   Efficiency                                        
______________________________________                                    
1            --         70                                                
2            FeCl.sub.3 74                                                
3            FeSO.sub.4 83                                                
4            Fe(NO.sub.3).sub.3                                           
                        81                                                
5            Al(NO.sub.3).sub.3                                           
                        71                                                
6            Ca(NO.sub.3).sub.2                                           
                        76                                                
7            NaAl(SO.sub.4).sub.2                                         
                        78                                                
8            Na.sub.2 SO.sub.4                                            
                        74                                                
9            Zn(NO.sub.3).sub.2                                           
                        77                                                
______________________________________                                    

Claims (7)

We claim:
1. A method for purifying a gas containing sulphur dioxide components therein, which method comprises contacting said gas with a mixture consisting of (i) a solid absorbent and (ii) a liquid, hydrous phase, which liquid phase is derived from a hygroscopic salt selected from the group consisting of FeCl3, Fe(NO3)3, Fe(NO3)2, Al(NO3)3, Ca(NO3)2, Mg(ClO3)2, MnCl2, K2 SO4.MgSO4, NaAl(SO4)2, NaClO, Na3 PO4, Na2 SiO3, Na2 SO4, and Zn(NO3)2 which hygroscopic salt is thermodynamically stable at the prevailing water partial pressure and temperature of said gas and which at least partly covers said solid absorbent, and preparing said mixture by adding to said solid absorbent said hygroscopic salt.
2. A method as defined in claim 1, wherein said gas consists of flue gas, said purifying process comprises a drying and absorption step, and a dust separation and secondary absorption step, and said solid absorbent is in an absorption liquid, and said absorption liquid and said liquid phase are added to said flue gas, said hygroscopic salt under conditions prevailing in the dust separator being adapted to distribute said liquid phase over the surface of said solid absorbent.
3. A method as defined in claim 1 or 2 wherein said sulphur dioxide components of said gas react with said solid absorbent to produce reaction products, and said liquid phase is aqueous and has good solubility for reactants and reaction products.
4. A method as defined in claim 2, wherein said added hygroscopic salt constitutes a maximum of 20 percent by volume of said solid absorbent present at said dust separator step.
5. A method as defined in claim 1 or 2 wherein said solid absorbent is selected from the group consisting of calcium hydroxide, calcium carbonate, magnesium calcium carbonate, sodium carbonate, sodium hydroxide or mixtures thereof.
6. A method as defined in claim 2 wherein said contacting step comprises atomizing said absorption liquid, and said hygroscopic salt is mixed in said absorption liquid prior to its atomization.
7. The method of claim 2, wherein said added hygroscopic salt constitutes a maximum of 5 percent by volume of said solid absorbent present at said dust separator.
US06/303,462 1981-09-18 1981-09-18 Method of purifying flue gases from sulphur dioxide Expired - Fee Related US4454102A (en)

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Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2162162A (en) * 1984-07-27 1986-01-29 Hitachi Shipbuilding Eng Co Method for purifying exhaust gas
US4600568A (en) * 1985-03-22 1986-07-15 Conoco Inc. Flue gas desulfurization process
US4603037A (en) * 1985-03-22 1986-07-29 Conoco Inc. Desulfurization of flue gas from multiple boilers
US4604269A (en) * 1985-03-22 1986-08-05 Conoco Inc. Flue gas desulfurization process
US4795619A (en) * 1987-03-20 1989-01-03 Lerner Bernard J Removal of acid gases in dry scrubbing of hot gases
US4865828A (en) * 1988-09-28 1989-09-12 Lerner Bernard J Removal of acid gases in dry scrubbing of hot gases
CN100998947B (en) * 2006-12-30 2010-08-11 东北大学 Magnesium oxide base calalytic-absorber for denitrogen of smoke and its preparation method
EP2711069A2 (en) 2012-09-20 2014-03-26 Lab Sa Process and plant for flue gas purification and electricity generation
CN105126567A (en) * 2014-10-11 2015-12-09 黄立维 Method and device for removing nitric oxide and sulfur oxide from gas flow
CN114682067A (en) * 2020-12-26 2022-07-01 黄华丽 Device and process for removing nitric oxide in airflow

Citations (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3261662A (en) * 1963-05-03 1966-07-19 Rosenblads Patenter Ab Absorption of sulphur dioxide and separation of ashes from combustion gases obtained by combustion of magnesium wastelye
DE1259845B (en) * 1960-12-14 1968-02-01 Pintsch Bamag Ag Process for the regeneration of activated carbon loaded with hydrogen sulphide and an organic solvent from exhaust air or oxygen-containing gases
US3416293A (en) * 1967-06-22 1968-12-17 Catalysts & Chem Inc Sulfur adsorption
DE1544011A1 (en) * 1965-10-01 1969-06-26 Ehrenberg Dr Wolfgang Filter material for SO2 removal from exhaust gases
DE1669315A1 (en) * 1967-05-19 1971-02-25 Inst Waermetechnik Und Automat Process and device for removing sulfur dioxide and trioxide from smoke and exhaust gases
FR2181988A1 (en) * 1972-04-24 1973-12-07 Hitachi Ltd Hot acidic waste gas purifcn - by spraying with an aq alkaline soln, collecting formed powder and recycling effluent soln
US3882221A (en) * 1973-01-10 1975-05-06 Harold W Wilson Process for liquid gas reaction on acid undecomposable silicates
US3966878A (en) * 1973-11-08 1976-06-29 General Resource Corporation Method for removing pollutants from a gaseous mixture
US3976747A (en) * 1975-06-06 1976-08-24 The United States Of America As Represented By The United States Energy Research And Development Administration Modified dry limestone process for control of sulfur dioxide emissions
JPS5472771A (en) * 1977-11-22 1979-06-11 Toray Ind Inc Removing method of sulfur oxides
EP0005301A1 (en) * 1978-05-10 1979-11-14 Metallgesellschaft Ag Process for the removal of sulphur oxides from high-chloride flue gases
US4177158A (en) * 1978-02-13 1979-12-04 Chevron Research Company Method for producing an attrition-resistant adsorbent for sulfur dioxide, the resulting composition and a process using same
US4201751A (en) * 1975-05-06 1980-05-06 Heinz Gresch Gas purification
US4279873A (en) * 1978-05-19 1981-07-21 A/S Niro Atomizer Process for flue gas desulfurization

Patent Citations (16)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE1259845B (en) * 1960-12-14 1968-02-01 Pintsch Bamag Ag Process for the regeneration of activated carbon loaded with hydrogen sulphide and an organic solvent from exhaust air or oxygen-containing gases
US3261662A (en) * 1963-05-03 1966-07-19 Rosenblads Patenter Ab Absorption of sulphur dioxide and separation of ashes from combustion gases obtained by combustion of magnesium wastelye
DE1544011A1 (en) * 1965-10-01 1969-06-26 Ehrenberg Dr Wolfgang Filter material for SO2 removal from exhaust gases
DE1669315A1 (en) * 1967-05-19 1971-02-25 Inst Waermetechnik Und Automat Process and device for removing sulfur dioxide and trioxide from smoke and exhaust gases
US3416293A (en) * 1967-06-22 1968-12-17 Catalysts & Chem Inc Sulfur adsorption
DE1769639A1 (en) * 1967-06-22 1971-10-28 Catalysts & Chem Inc Process of sulfur adsorption
FR2181988A1 (en) * 1972-04-24 1973-12-07 Hitachi Ltd Hot acidic waste gas purifcn - by spraying with an aq alkaline soln, collecting formed powder and recycling effluent soln
US3882221A (en) * 1973-01-10 1975-05-06 Harold W Wilson Process for liquid gas reaction on acid undecomposable silicates
US3966878A (en) * 1973-11-08 1976-06-29 General Resource Corporation Method for removing pollutants from a gaseous mixture
US4201751A (en) * 1975-05-06 1980-05-06 Heinz Gresch Gas purification
US3976747A (en) * 1975-06-06 1976-08-24 The United States Of America As Represented By The United States Energy Research And Development Administration Modified dry limestone process for control of sulfur dioxide emissions
JPS5472771A (en) * 1977-11-22 1979-06-11 Toray Ind Inc Removing method of sulfur oxides
US4177158A (en) * 1978-02-13 1979-12-04 Chevron Research Company Method for producing an attrition-resistant adsorbent for sulfur dioxide, the resulting composition and a process using same
EP0005301A1 (en) * 1978-05-10 1979-11-14 Metallgesellschaft Ag Process for the removal of sulphur oxides from high-chloride flue gases
US4279873A (en) * 1978-05-19 1981-07-21 A/S Niro Atomizer Process for flue gas desulfurization
US4279873B1 (en) * 1978-05-19 1996-04-16 Karsten S Felsvang Process for flue gas desulferization

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2162162A (en) * 1984-07-27 1986-01-29 Hitachi Shipbuilding Eng Co Method for purifying exhaust gas
US4600568A (en) * 1985-03-22 1986-07-15 Conoco Inc. Flue gas desulfurization process
US4603037A (en) * 1985-03-22 1986-07-29 Conoco Inc. Desulfurization of flue gas from multiple boilers
US4604269A (en) * 1985-03-22 1986-08-05 Conoco Inc. Flue gas desulfurization process
US4795619A (en) * 1987-03-20 1989-01-03 Lerner Bernard J Removal of acid gases in dry scrubbing of hot gases
US4865828A (en) * 1988-09-28 1989-09-12 Lerner Bernard J Removal of acid gases in dry scrubbing of hot gases
CN100998947B (en) * 2006-12-30 2010-08-11 东北大学 Magnesium oxide base calalytic-absorber for denitrogen of smoke and its preparation method
EP2711069A2 (en) 2012-09-20 2014-03-26 Lab Sa Process and plant for flue gas purification and electricity generation
CN105126567A (en) * 2014-10-11 2015-12-09 黄立维 Method and device for removing nitric oxide and sulfur oxide from gas flow
CN105126567B (en) * 2014-10-11 2019-08-20 黄立维 A kind of method and device thereof for removing denitrification and oxysulfide from air-flow
CN114682067A (en) * 2020-12-26 2022-07-01 黄华丽 Device and process for removing nitric oxide in airflow

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